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      A new mechanism for atmospheric mercury redox chemistry: implications for the global mercury budget

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          Abstract

          Mercury (Hg) is emitted to the atmosphere mainly as volatile elemental Hg<sup>0</sup>. Oxidation to water-soluble Hg<sup>II</sup> plays a major role in Hg deposition to ecosystems. Here, we implement a new mechanism for atmospheric Hg<sup>0</sup> ∕ Hg<sup>II</sup> redox chemistry in the GEOS-Chem global model and examine the implications for the global atmospheric Hg budget and deposition patterns. Our simulation includes a new coupling of GEOS-Chem to an ocean general circulation model (MITgcm), enabling a global 3-D representation of atmosphere–ocean Hg<sup>0</sup> ∕ Hg<sup>II</sup> cycling. We find that atomic bromine (Br) of marine organobromine origin is the main atmospheric Hg<sup>0</sup> oxidant and that second-stage HgBr oxidation is mainly by the NO<sub>2</sub> and HO<sub>2</sub> radicals. The resulting chemical lifetime of tropospheric Hg<sup>0</sup> against oxidation is 2.7 months, shorter than in previous models. Fast Hg<sup>II</sup> atmospheric reduction must occur in order to match the ∼  6-month lifetime of Hg against deposition implied by the observed atmospheric variability of total gaseous mercury (TGM  ≡  Hg<sup>0</sup> + Hg<sup>II</sup>(g)). We implement this reduction in GEOS-Chem as photolysis of aqueous-phase Hg<sup>II</sup>–organic complexes in aerosols and clouds, resulting in a TGM lifetime of 5.2 months against deposition and matching both mean observed TGM and its variability. Model sensitivity analysis shows that the interhemispheric gradient of TGM, previously used to infer a longer Hg lifetime against deposition, is misleading because Southern Hemisphere Hg mainly originates from oceanic emissions rather than transport from the Northern Hemisphere. The model reproduces the observed seasonal TGM variation at northern midlatitudes (maximum in February, minimum in September) driven by chemistry and oceanic evasion, but it does not reproduce the lack of seasonality observed at southern hemispheric marine sites. Aircraft observations in the lowermost stratosphere show a strong TGM–ozone relationship indicative of fast Hg<sup>0</sup> oxidation, but we show that this relationship provides only a weak test of Hg chemistry because it is also influenced by mixing. The model reproduces observed Hg wet deposition fluxes over North America, Europe, and China with little bias (0–30 %). It reproduces qualitatively the observed maximum in US deposition around the Gulf of Mexico, reflecting a combination of deep convection and availability of NO<sub>2</sub> and HO<sub>2</sub> radicals for second-stage HgBr oxidation. However, the magnitude of this maximum is underestimated. The relatively low observed Hg wet deposition over rural China is attributed to fast Hg<sup>II</sup> reduction in the presence of high organic aerosol concentrations. We find that 80 % of Hg<sup>II</sup> deposition is to the global oceans, reflecting the marine origin of Br and low concentrations of organic aerosols for Hg<sup>II</sup> reduction. Most of that deposition takes place to the tropical oceans due to the availability of HO<sub>2</sub> and NO<sub>2</sub> for second-stage HgBr oxidation.

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              Interactions between mercury and dissolved organic matter--a review.

              Dissolved organic matter (DOM) interacts very strongly with mercury, affecting its speciation, solubility, mobility, and toxicity in the aquatic environment. Strong binding of mercury by DOM is attributed to coordination of mercury at reduced sulfur sites within the organic matter, which are present at concentrations much higher than mercury concentrations found in most natural waters. The ability of organic matter to enhance the dissolution and inhibit the precipitation of mercuric sulfide, a highly insoluble solid, suggests that DOM competes with sulfide for mercury binding. This is confirmed by very high conditional stability constants for mercury-organic sulfur (RSHg+) complexes (10(25)-10(32)) recently reported in literature. DOM appears to play a key role in the photochemical reduction of ionic mercury to elemental mercury and subsequent reoxidation of elemental mercury to ionic mercury, thus affecting volatilization loss and bioavailability of mercury to organisms. DOM affects the production and bioaccumulation of methylmercury, the most bioaccumulative mercury species in fish.
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                Author and article information

                Journal
                Atmospheric Chemistry and Physics
                Atmos. Chem. Phys.
                Copernicus GmbH
                1680-7324
                2017
                May 29 2017
                : 17
                : 10
                : 6353-6371
                Article
                10.5194/acp-17-6353-2017
                28537e98-e88b-4213-bb20-8791ed8d1c30
                © 2017

                https://creativecommons.org/licenses/by/3.0/

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